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Frontiers of Chemical Science and Engineering

ISSN 2095-0179

ISSN 2095-0187(Online)

CN 11-5981/TQ

Postal Subscription Code 80-969

2018 Impact Factor: 2.809

Front. Chem. Sci. Eng.    2021, Vol. 15 Issue (4) : 984-997    https://doi.org/10.1007/s11705-020-2000-3
RESEARCH ARTICLE
Activated carbon-hybridized and amine-modified polyacrylonitrile nanofibers toward ultrahigh and recyclable metal ion and dye adsorption from wastewater
Fengli Li1, Chuang Chen1, Yuda Wang1, Wenpeng Li1, Guoli Zhou1(), Haoqin Zhang1, Jie Zhang1(), Jingtao Wang1,2
1. School of Chemical Engineering, Zhengzhou University, Zhengzhou 450001, China
2. Henan Institute of Advanced Technology, Zhengzhou University, Zhengzhou 450003, China
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Abstract

Nanofibers with high specific surface area and chemical stability have broad prospects in the applications of adsorption. However, the adsorption capacity is limited by the scarcity of adsorption groups and storage space. Herein, the activated carbon-hybridized and amine-modified nanofibers are prepared by integrating activated carbon (AC) and polyacrylonitrile (PAN) via electrospinning method and the subsequent amination, which could provide additional storage space and adsorption groups for ultrahigh adsorption capability. Thus, the obtained amine-rich porous PAN nanofibers (APAN/AC) readily realized the ultrahigh adsorption capacity for metal ions and dyes in wastewater. Specifically, the adsorption capacity of APAN/AC nanofibers were 284 mg·g−1 for Cr(VI) and 248 mg·g−1 for methyl orange, which were almost 2 and 4 times than that of amine-modified nanofibers (APAN) and carbon-hybridized nanofibers (PAN/AC), respectively. Moreover, the AC inhibited the chain mobility of polymer matrix and thereby endowing APAN/AC nanofibers with excellent recyclability. The adsorption capability retained 80% after nine adsorption-desorption cycles. The adsorption kinetics and corresponding mechanism were further explored. This strategy combines the advantages of polymer nanofibers and AC, opening a new avenue for developing next-generation absorbent materials.

Keywords carbon-hybridized and amine-modified nanofibers      polyacrylonitrile      metal ions and dyes      wastewater      adsorption kinetics     
Corresponding Author(s): Guoli Zhou,Jie Zhang   
Just Accepted Date: 10 November 2020   Online First Date: 04 January 2021    Issue Date: 04 June 2021
 Cite this article:   
Fengli Li,Chuang Chen,Yuda Wang, et al. Activated carbon-hybridized and amine-modified polyacrylonitrile nanofibers toward ultrahigh and recyclable metal ion and dye adsorption from wastewater[J]. Front. Chem. Sci. Eng., 2021, 15(4): 984-997.
 URL:  
https://academic.hep.com.cn/fcse/EN/10.1007/s11705-020-2000-3
https://academic.hep.com.cn/fcse/EN/Y2021/V15/I4/984
Fig.1  Scheme 1 Schematic diagram of the whole preparation process for APAN/AC nanofibers.
Fig.2  Surface SEM images of (a), (b) PAN and (c), (d) APAN/AC nanofibers; AFM images of (e) PAN and (f) APAN/AC nanofibers.
Fig.3  (a) FTIR pattern and (b) XRD spectra of AC, PVP, PAN, PAN/PVP/AC, PAN/AC and APAN/AC nanofibers, and (c) C 1s and (d) N 1s spectra of APAN/AC nanofibers.
Samples N/% C/% H/% C/N
PAN/PVP/AC 15.78 60.99 6.81 3.87
PAN/AC 17.93 61.63 5.38 3.44
APAN/AC 18.56 61.72 6.30 3.33
Tab.1  Element analysis results of PAN/PVP/AC, PAN/AC and APAN/AC nanofibers
Samples Specific surface area/(m2·g−1) Pore volume/(cm−3·g−1)
PAN
PAN/AC
APAN/AC
32.3
68.5
76.2
0.039
0.105
0.165
Tab.2  Specific surface area and pore volume of PAN, PAN/AC and APAN/AC nanofibers
Fig.4  (a) N2 adsorption/desorption isotherm and (b) pore size distribution of PAN, PAN/AC and APAN/AC nanofibers, and (c) the water contact angles of APAN and APAN/AC nanofibers.
Fig.5  (a) The DpH against pHinitial plot for PAN/AC and APAN/AC nanofibers, and (b) the adsorption capacity of APAN/AC nanofibers at different pH.
Fig.6  Adsorption isotherms plots for APAN/AC, APAN, and PAN/AC nanofibers of (a) Cr(VI) and (b) MO, and Langmuir plots of (c) Cr(VI) and (d) MO.
Adsorbate Langmuir isotherm Freundlich isotherm
qcal /(mg·g−1) KL /(L·mg−1) R2 KF n R2
APAN Cr(VI) 126 0.71 0.9993 43.35 4.29 0.6068
MO 115 0.43 0.9997 34.32 3.89 0.6063
PAN/AC Cr(VI) 53 0.26 0.9997 21.91 3.15 0.8993
MO 63 0.37 0.9992 21.79 2.98 0.7951
APAN/AC Cr(VI) 288 0.62 0.9995 78.07 5.79 0.6889
MO 254 0.36 0.9996 59.34 4.63 0.6793
Tab.3  Adsorption isotherms parameters for APAN, PAN/AC and APAN/AC nanofibers
Fig.7  Adsorption kinetics plots for APAN/AC, APAN, and PAN/AC nanofibers of (a) Cr(VI) and (b) MO, pseudo-second-order kinetic plots of (c) Cr(VI) and (d) MO, and Weber–Morris kinetics plots of (e) Cr(VI) and (f) MO.
Adsorbate Pseudo-first-order model Pseudo-second-order model Weber–Morris model
K1 R2 K2 R2 K3.1 R2 K3.2 R2
APAN Cr(VI) 0.029 0.8271 2.03×10-4 0.9913 10.89 0.9935 0.25 0.9905
MO 0.036 0.6495 1.86×10-4 0.9937 10.02 0.9628 0.63 0.9802
PAN/AC Cr(VI) 0.029 0.7317 1.53×10-4 0.9926 4.57 0.9998 1.31 0.9956
MO 0.026 0.7596 1.56×10-4 0.9951 5.81 0.9803 1.23 0.9939
APAN/AC Cr(VI) 0.018 0.9455 2.13×10-4 0.9973 40.21 0.9945 2.23 0.9605
MO 0.023 0.7549 1.87×10-4 0.9916 26.12 0.9987 0.41 0.9963
Tab.4  Adsorption kinetics parameters for APAN, PAN/AC and APAN/AC nanofibers
Item Temperature/K DG0/(kJ·mol−1) DH0/(kJ·mol−1) DS0/(J·mol−1·K−1)
Cr(VI) 293 ?4.45
?6.47
?8.49
?10.51
54.76 202.09
303
313
323
MO 293 ?4.17
?6.42
?8.67
?10.92
61.69 224.78
303
303
323
Tab.5  The thermodynamic parameters of APAN/AC nanofibers
Fig.8  FTIR spectra of pure APAN/AC nanofibers and after adsorption.
Fig.9  Scheme 2 Schematic illustration of APAN/AC nanofibers for Cr(VI) and MO adsorption in wastewater.
Fig.10  (a) Effect of coexisting ions and (b) regeneration cycle study.
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